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Integrating Soil Ecological Knowledge Into Restoration Management Liam Heneghan,1,2 Susan P

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Integrating Soil Ecological Knowledge Into Restoration Management Liam Heneghan,1,2 Susan P Integrating Soil Ecological Knowledge into Restoration Management Liam Heneghan,1,2 Susan P. Miller,3 Sara Baer,4 Mac A. Callaham, Jr.,5 James Montgomery,1 Mitchell Pavao-Zuckerman,6 Charles C. Rhoades,7 and Sarah Richardson1 Abstract components of the soil system can be useful in the restora- The variability in the type of ecosystem degradation and tion of a site, especially when the restoration goal is the specificity of restoration goals can challenge restora- loosely defined in terms of the species and processes that tionists’ ability to generalize about approaches that lead management seeks to achieve. These single-factor manip- to restoration success. The discipline of soil ecology, which ulations may in fact produce cascading effects on several emphasizes both soil organisms and ecosystem processes, ecosystem attributes and can result in unintended recov- has generated a body of knowledge that can be generally ery trajectories. When complex outcomes are desired, useful in improving the outcomes of restoration despite intentional and holistic integration of all aspects of the soil this variability. Here, we propose that the usefulness of knowledge is necessary. We provide a short roster of ex- this soil ecological knowledge (SEK) for restoration is amples to illustrate that SEK benefits management and best considered in the context of the severity of the origi- restoration of ecosystems and suggest areas for future nal perturbation, the goals of the project, and the resil- research. ience of the ecosystem to disturbance. A straightforward manipulation of single physical, chemical, or biological Key words: ecosystem processes, feedbacks, soil ecology. Introduction et al. 2006). Published restoration science in the primary Restoration ecologists have long recognized the integral literature commonly includes soil information associated role of soil, particularly in its physical and chemical with pre-restoration site assessment and the evaluation of aspects, in the successful revegetation of degraded sites specific soil amendments (Callaham et al. 2008). Recovery (Jordan et al. 1987). However, explicit incorporation of of nutrient capital or biogeochemical processes also moti- soil ecological knowledge (SEK), which acknowledges vates restoration activities, but examples where integrated interactions among the principal components of the soil SEK has been employed are uncommon. system as well as feedback between the aboveground and In this article, we discuss restoration practice and re- belowground ecosystem processes, into restoration re- search that is informed by SEK. The term ‘‘soil ecological mains in a relatively early stage of development (Aronson knowledge’’ is used to indicate perspectives from the disci- et al. 1993; Harris et al. 2006; Wardle & Peltzer 2007). pline of soil ecology that integrate soil physical, chemical, Despite earlier attempts to demonstrate the importance of and biological factors and processes in context of plant– a soil’s perspective for restoration efforts, a recent and soil feedback. In particular, it is knowledge from soil useful review of research on restoration ecology makes ecology that can be used explicitly to inform restoration only scattered references to soil processes and biota (Falk practice. A restoration approach that employs more sophisticated SEK differs from simpler approaches that consider soil factors in isolation or that separates above- 1 DePaul University, Environmental Science Program, Chicago, IL 60614, U.S.A. ground from belowground ecosystem processes. We dis- 2 Address correspondence to L. Heneghan, email [email protected] cuss a classification of restoration approaches arrayed 3 Millroad Ecological Services, 2200 Three Oaks Court, Fort Collins, CO 80526, U.S.A. along a gradient of increasing need for knowledge of soil 4 Department of Plant Biology, Southern Illinois University, Carbondale, ecology to attain the ecosystem structure and function of IL 62901, U.S.A. 5 USDA-Forest Service, Forestry Sciences Laboratory, Athens, GA 30602, a particular reference condition. Additionally, we identify U.S.A. promising new research areas, where restoration projects 6 Biosphaere 2, PO Box 210088, University of Arizona, Tucson, AZ 85721, U.S.A. may advance our understanding of soil ecology and where, 7 USDA Forest Service Rocky Mountain Research Station, Fort Collins, reciprocally, a deepened knowledge of the soil system CO 80526, U.S.A. may enhance restoration practice. Ó 2008 Society for Ecological Restoration International The discipline of soil ecology has deep roots in soil sci- doi: 10.1111/j.1526-100X.2008.00477.x ence and organismal biology. Soil ecologists have merged 608 Restoration Ecology Vol. 16, No. 4, pp. 608–617 DECEMBER 2008 Integrating Soil Ecological Knowledge these traditional disciplines to understand ecosystem pro- cesses, which have provided tools for elucidating concepts central to ecology as a whole (Coleman et al. 2004; Lavelle & Spain 2001; Bardgett 2005). For example, rela- tionships between biodiversity and ecosystem functioning have been tested using model soil ecosystems (Lavelle 1996; Bengtsson 1998; Lawton et al. 1998; Setala et al. 1998; Behan-Pelletier & Newton 1999; Heneghan et al. 1999; Zak et al. 2003; Fitter et al. 2005). Furthermore, perspectives in soil ecology that focus on the reciprocal feedback of above- and belowground biota and pro- cesses have become increasingly central to ecology (e.g., Casper & Jackson 1997; Klironomos 2002; Setala 2002; Wardle 2002; Bardgett & Wardle 2003; Van Der Putten 2003; Wardle et al. 2004). The holistic perspective that integrates organismic and ecosystem processes at the core of soil ecology has provided explanations for patterns in the distribution, abundance, and composi- tion of species, a fundamental organizing tenet in ecol- ogy (Tilman 1982; Bever 1994; Bever et al. 1997; Baer et al. 2005). Soil biota is directly involved in key ecosystem pro- cesses (e.g., decomposition and nutrient cycling), and understanding such interactions has provided one of the unifying themes of soil ecological research over the past few decades (Swift et al. 1979; Wardle 2002). Because of the demonstrated key role in the regulation of ecosystem processes, application of insights from soil ecology has been useful in situations where desired outcomes go beyond simple enhancement of single factors such as pro- ductivity. For instance, soil ecology has made a substantial contribution to alternative agricultural practices, such as no-till cropping systems, by integrating conservation of physical, chemical, and biological properties of soil Figure 1. Framework for linking (a) SEK to existing theoretical (Coleman et al. 2002). In this case, soil ecologists have models of ecosystem restoration (b and c). (a) When sites are heavily demonstrated the importance of shifts from bacterial to degraded, improved soil function may be achieved by simple single- fungal channels in soil food webs for the development of factor manipulations of a given chemical (C), physical (P), or bio- soil structure, soil organic matter (SOM) sequestration, logical (B) attribute. For greater progress toward a target condition, an increase in the degree of complex SEK is required (and the and modulation of soil nutrient availability (Hendrix et al. consideration of interactions between P, C, and B components will 1986; Beare et al. 1995). Lessons gained from agroecology be critical). (b) Physical and biological thresholds which must be have inspired recent investigations of changes in microbial overcome if restoration is to be successful (modified from Whisenant community structure following cessation of tillage and 1999). (c) The integral relationship between structural and functional restoration of native vegetation (Allison et al. 2005; attributes in ecosystem restoration (modified from Bradshaw 1987). McKinley et al. 2005). See text for examples and further illustration. Contribution of Soil Ecology to Restoration— characteristics of a specified reference condition. Signifi- A Classification cantly degraded sites generally require active consider- We propose that the relationship between SEK and resto- ation of the soil, e.g., remediating oil spills (Kuyukina ration may be best considered in the context of the sever- et al. 2003). Site remediation in circumstances where re- ity of the original perturbation, the goals of the project, storing pre-disturbance above- and belowground structure and the resilience of the original ecosystem to disturbance and function is not a priority and may require a mani- (Fig. 1). Our conceptual model builds on previous models pulation of a single physical, chemical, or biological part of ecosystem restoration (Bradshaw 1987; Whisenant of the soil system to improve a system’s state relative to 1999; Hobbs & Harris 2001). We surmise that the utility of the perturbed state. For example, when a system has been SEK for achieving a restoration goal depends on the so severely perturbed that plants simply will not grow degree to which the restoration intent aims to achieve (e.g., on soils contaminated by heavy metals, oil spills, DECEMBER 2008 Restoration Ecology 609 Integrating Soil Ecological Knowledge brine scars), the restoration goal may be limited to Integration of Soil Knowledge: Case Studies reclaiming a specific structure or process to enable revege- Hobbs and Harris (2001) and Hobbs and Norton (2004) tation. This may be achieved through ripping, tilling, or suggest that abiotic and biotic constraints may stall the contouring
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